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Table of Contents
Getting Started
Glossary
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| Metal removal fluids need to be checked often to make sure that the
fluid is performing as it should. MRF must be kept in good condition. That means keeping
it free of contaminants, keeping fluid components at the proper levels, and testing for
various chemical and physical properties. |
Testing metal removal fluids
| Some chemical tests of fluid condition can be done only in a
laboratory using special instruments and apparatus, but some tests can be done in
the shop with relatively inexpensive equipment. Dissolved oxygen, pH, and conductivity can
all be measured by instruments that will fit in a shirt pocket; these are available from
laboratory supply houses. These require frequent calibration, but the procedures are
simple and the standards are inexpensive and reliable. |
|
types of tests
concentration
alkalinity
conductivity
pH
oil concentration
emulsion stability
appearance
specific ingredients
salts
dirt
microbes
how often to test
obtaining
samples
concentration
checks:
acid split
refractive index
chemical titration
acid split
refractive index
chemical
titration
chemical and physical properties tested for
alkalinity
conductivity
pH
oil concentration
emulsion
stability
appearance
specific
ingredients tested for
contaminants
chemical
products
oil
non-process
salts
dirt
gravimetric
testing
centrifuge testing
microbes:
plate counts
dipsticks
dissolved oxygen
catalase levels
acceptable level of microbes
plate counts
dipsticks
dissolved oxygen
catalase levels
level of microbes
frequency of testing by sump
size:
miniature
small
small-medium
medium
large |
| Many suppliers can also provide simple titration kits or test papers that
measure emulsifier content or alkalinity in a solution. These kits can provide a quick
check for strength (concentration) and condition. |
What kinds of tests are
performed?
It is usual to check for
 | fluid concentration |
|
 | physical and/or chemical properties of the bulk fluid |
|
 | specific ingredient concentrations |
|
 | contamination levels |
|
How are samples of the fluid obtained for testing?
| MRF samples should be drawn and tested in the same manner each time, with
samples taken at the same time of day when possible. Each system should have a sampling
valve in an accessible area on the clean MRF supply header. The sampling valve should be
opened and MRF purged for 30 seconds before the sample is taken. No hose should be
attached to the valve. If the system has vacuum filtration, the vacuum should be recorded
when the sample is taken (contaminant levels may be higher if the filter medium has just
advanced or "indexed"). If the system has pressure filtration, the pressure drop
across the filter should be recorded |
Why are concentration checks performed?
| The single most important fluid characteristic is concentration. At the
proper dilution, the fluid contains adequate levels of biocides, corrosion inhibitors,
cleaners, and lubricants to perform as expected. If the concentration is too weak, the
fluid simply will not perform as it should. The fluid will go rancid, parts and machines
will rust, and tool life will be poor. If the concentration is too strong, problems with
foam and residue on machined parts can arise. Concentrations that are too strong can also
create the potential for adverse health effects to exposed employees, such as dermatitis
or respiratory effects. |
How are concentration
checks performed?
| Concentration is commonly determined by measuring some easily determined
fluid property and using the result to estimate the dilution factor for the fluid as a
whole. The test may be as unsophisticated as measuring the refractive index; it may
require simple lab equipment and chemicals (acid split); or it may require a titration
involving volumetric devices, and chemical reagents and solvents may be used. All these
tests give only gross estimates, and their results should be used with caution. |
Acid split
This test is performed only for semisynthetic and soluble oil metal
removal fluids. In a centrifuge/acid split, sulfuric acid is added with care (to avoid
spattering) to the sample in order to destroy the emulsion, and both are placed in a
Winthrop tube or Babcock bottle. The tube is spun in a low-speed centrifuge for 15
minutes. The oil will separate from the water phase and form a layer at the top of the
tube. The concentration is determined by the ratio of oil to water. Note that any tramp
oil will be read as metal removal fluid.
| Refractive Index |
|
| Any chemical present in solution will cause a change in refractive index
relative to water. Good correlations exist between refractive index and concentration in
"fresh," uncontaminated fluids. As soon as any contaminant is introduced, the
strength of this correlation is compromised. In general, the refractive index gives a
measure of the maximum concentration of a fluid; the actual concentration may well be
less. No other reliable information can be learned from this test. |
| Chemical Titration |
The amounts of fluid components in a diluted fluid can be determined by
volumetric titration. The fluid concentration can then be estimated by assuming that all
components are present in the diluted mix in the same ratios as in the unused fluid. The
method may be as simple as titration with acid to determine the alkalinity of the fluid.
At the other extreme, the method may involve reaction of the anionic emulsifiers in a
fluid with a known amount of a cationic polymer. These methods commonly involve extraction
of the sample with an organic solvent which may be toxic and unsuitable for use by
untrained personnel outside a laboratory.
| All these tests can be subject to interferences by
contaminants in the fluid. Ideally, more than one test will be used to check for
concentration. |
|
| How often should concentration
checks be performed? |
|
| Concentration checks should be performed dailycertainly
not less than twice a week. The frequency depends on the size of the system sump and past
history of the systems performance. |
|
| What chemical and physical
properties of the bulk fluid, besides concentration, are measured? |
|
|
Such properties include
| The major advantage of these measurements is that they are easily done
with minimal equipment. It is important to remember, however, that a single result
may not indicate anything particularly useful about the fluid condition. The tests can be
used as a way to confirm what another test has indicated, or to alert you to the
possibility of a problem. |
|
| It is assumed in this fluid management guide that those who need to be
familiar with testing procedures will be familiar with the terms used in the following
discussions of the properties listed above. |
Alkalinity
| For fresh, uncontaminated fluids, the correlation between alkalinity and
concentration is good. Alkalinity will increase as a fluid ages because the alkaline
components of a fluid are less likely to be stripped out by tramp oil, water hardness and
other contaminants. |
| Many contaminants are themselves alkaline. However, alkalinity is a
valuable fluid property to follow. Sudden increases in alkalinity signal contamination.
Divergence of alkalinity from the anionic concentration signals possible fluid
instability. Once the behavior of a system is known, it is possible to use alkalinity as a
signal that fluid stability problems are imminent. The levels of alkalinity can also
indicate that cases of dermatitis in employees exposed to the MRF may be about to occur. |
Conductivity
| The information gained from measuring conductivity is similar to that from
alkalinity, but conductivity reflects the presence of all ions, while alkalinity is
sensitive only to materials that are alkaline. On the other hand, alkalinity responds to
materials that are not ionic, so the two tests confirm and complement one another. |
| Conductivity increases with use, reflecting the buildup of salts from the
evaporation of make-up water over time. The conductivity of a system will increase
steadily until solubility limits are reached. Thereafter, the conductivity remains
constant; inorganic ions are lost through precipitation, and organic ions may be salted
out of the aqueous phase into the oil phase. Once this loss of ions is taking place, fluid
performance degrades and the emulsion can become unstable. |
pH
| Alkalinity and pH are strongly related, but are distinct properties. The
pH of a fluid is the same for any size sample. The alkalinity is measured by the volume of
acid needed to titrate the sample to a given pH value and is dependent on the sample size.
A pH meter should be used. The pH of a working fluid in good condition will tend to be
around 8.8-9.2. However, the fluid supplier should be contacted for the appropriate pH
range. Some fluids are designed to operate outside the pH range of 8.8-9.2. |
| The usual cause of pH drops is microbial growth, with resulting formation
of metabolic acids. Keeping pH levels at 8.8 or above is an effective means of controlling
bacterial growth and microbial odors. (Exceptions are some fluids for non-ferrous
metals designed to be used at lower pH levels.) Caustic (sodium or potassium hydroxide) or
sodium borate can be added to raise system pH. System pH should be monitored at the same
frequency as concentration. |
Oil concentration
| It is common to estimate the concentration of soluble oils by splitting
the emulsion with sulfuric acid and separating the oil by centrifugation (see p.44).
Obviously, tramp oil will interfere with this test. |
| This method can be used to estimate tramp oil levels by testing for
concentration by an independent method and calculating the amount of oil expected from the
fluid alone and subtracting this from the observed amount of oil. Erroneous tramp oil
levels are calculated if contaminants bias the results of the independent test or if the
emulsion is unstable. When the calculated tramp oil level is negative, there is a clear
signal that the fluid is unstable or that contaminants are interfering with the
independent concentration check. |
Emulsion stability
| Emulsion stability can be evaluated by allowing a sample to stand
undisturbed overnight or by centrifuging and observing the amount of free oil or cream
that floats to the top. A sample is spun on a low-speed centrifuge (3000 RPM) for 15
minutes. The tramp oil will separate at the top of the liquid, the cream will separate to
form the next level, and the suspended solids will settle to the bottom. A translucent or
watery looking layer at the lower part of the tube indicates a weak (unstable) emulsion.
This procedure should be done daily until the results are consistent enough to reduce the
frequency. Tests should be done a minimum of twice a week. |
| Once the emulsion has become unstable, it may be possible to add
emulsifiers to restabilize the fluid. However, the performance of the fluid will be
compromised and the problem may recur, especially if the root cause has not been
corrected. Excessive centrifugation can split the emulsion. |
Physical appearance
| The physical appearance of a fluid can provide indications of product
problems. Look for cream or free oil layers floating to the top of the fluid, changes in
appearance from translucent to milky, formation of haze (indicates a problem with fluid
stability) or gray to black color formation (indicates microbial growth). |
For what specific
ingredients is the fluid tested?
In many cases, it is possible to check for individual fluid components for
which specific analytical tests have been developed. It is important to know that
interference will be present when contaminants contain chemical components that are
similar to those in the fluid. Also, wet chemical methods may require the use of toxic
chemicals that are not appropriate for use in some metalworking plants. Instrumental
methods may require the use of sophisticated and expensive equipment. Specific chemical
tests can be done by the suppliers facility, but the data may be several days old
before it is available to the user. The general tests and their applicability are given in
the Table.
|
Class |
Titration |
HPLC |
Electrochemical |
Spot Test |
Anionic surfactant |
X |
X |
X |
|
Cationic surfactant |
X |
X |
|
|
Nonionic surfactant |
X |
X |
X |
|
Carboxylic Acids |
|
X |
|
|
Biocides |
|
X |
X |
X |
What contaminants are looked for in a contamination check? |
Contaminants may be chemical products, oils, dirt, or material
not related to the metal removal process at all; they may also be microbial.
|
Chemical products, oils, dirt,
and non-process contaminants
|
| Many chemical products can be found in metalworking plants. It
is best to assume that all of these can and do get into sumps and become part of the
fluid. These include |
hydraulic oils
spindle oils
way lubes
gear lubes
greases
rust preventatives
parts cleaners
floor cleaners
| Oil that gets into the metal removal fluid is
called tramp oil and should be
removed by skimming, coalescence filters, or centrifugation. See oil concentration. |
| Non-process contaminantseverything from
bacteria, mold, and yeasts, to food scraps, cigarette butts, and shop ragsalso find
their way into the MRF system. |
| Salts accumulate
in fluids through evaporation of water or by being carried in on work pieces. At high
ionic strengths, emulsions are less stable, and the fluid performance will decline.
Chlorides and sulfates will cause corrosion problems at relatively low levels (about 100
PPM). Magnesium and calcium ions will react with emulsifiers to form hard water deposits. |
The most reliable method for estimating individual ions is ion
chromatography. Heavy metal ions may be determined by X-ray or atomic absorption
spectroscopy. There are titration and colorimetric methods for many ions, but these are
subject to interference by normal fluid components.
|
Dirt, in the form of metal
fines or grinding wheel grit, is suspended in the fluid and is removed from the fluid by
filtration or settling. The level of dirt (total suspended solids) in the fluid is a
measure of the efficiency of the filtering system, so the amount of dirt is often checked.
| It can be estimated visually by centrifugation of a sample or
gravimetrically from a filtered sample. |
| To test gravimetrically, a 100-mL sample of MRF is filtered
through a membrane of known micrometer size (usually 8 micrometers). The dirt captured on
the membrane is weighed and reported in parts per million by weight. |
|
| A problem with the gravimetric test is that particles less than 8
micrometers pass through the membrane and are never included in the PPM results. In cast
iron and cast aluminum, a significant amount of the contaminant may be less than 8
micrometers and will go undetected. Previously, it was thought that small particles below
8 micrometers were not as detrimental to machining operations as larger particles. Recent
studies have indicated this is not true; in fact, particles smaller than 8 micrometers may
cause more problems than larger particles. Most filter systems for machining operations
are effective at removing particles over 20 micrometers. But as the particle size
decreases, a filter systems efficiency in removing particles drops. |
|
| With centrifuge testing (see emulsion
stability), the total solids reported include many particles in the 1- to
10-micrometer range that the filter cannot efficiently remove. The particulate collected
in the bottom of the tube is then reported in parts per million by volume. |
|
| Plants are encouraged to use both methods of testing, gravimetric and
centrifuge. The centrifuge method should be used regularly to monitor the stability and
quality of the MRF. The gravimetric method should be used periodically and when quality
problems arise to verify filter function. A gravimetric test through a series of different
membranes (1, 8, 20, 40 micrometers, for example) is a better indication of filter
performance. The presence of a great number of large particles would indicate a filter or
media problem. |
Dirt levels can be reduced by use of additives or by adjusting filter parameters.
Microbes
| Water-diluted metal removal fluids can support the growth of some
microorganisms, as can straight oils contaminated by water. The microorganisms found in
metal removal fluids are the same common species that are found in soil, air and on the
human body. Because MRF systems can support the growth of microorganisms, it is important
to make periodic measurements of their concentration in water-diluted fluids. If doubt
exists with miniature and small sumps, DCR (drain, clean, and replace) the fluid instead
of running the test. |
Whats the procedure for checking
for microbial contamination?
Checking for microbial contamination can be done in various ways:
 | plate counts |
|
 | dipsticks |
|
 | dissolved oxygen reading |
|
 | measurement of catalase levels |
|
Dilution plate counts
| Microbial levels may be estimated by preparing increasing dilutions of the
MRF in sterile nutrient solution, spreading a known amount of the different dilutions on
nutrient agar in Petri dishes, and incubating for two or three days. Each living organism
in the sample will multiply to form a visible colony. The number of colonies will be
related to the number of living organisms present in a milliliter of the starting fluid
and the dilution that produced a countable Petri dish. The results are normally reported
as colony-forming units per mL of fluid (CFU/mL). While a general-purpose nutrient medium
is used for most testing, the type of microorganism that will grow can be selected by the
choice of nutrients used. |
| Dilution plate counts have a disadvantage. Bacteria increase at an
exponential rate. During the 24 to 48 hours that the dipsticks are incubating, bacteria
counts can increase by orders of magnitude. If you suspect the significant bacterial or
fungal growth, it is better to act than to "wait and see." |
Dipsticks
| These are available with a general-purpose nutrient agar, or
a fungi specific agar, coated on a paddle and enclosed in a clear sterile tube. The paddle
is dipped into the sample, returned to its container, and incubated for two days. A dye
makes bacterial colonies more visible. Because there is no dilution of the fluid, the
number of colonies can be very high. The paddles are read by comparing their appearance to
reference pictures that were prepared from known concentrations of bacteria or fungi. |
| Bacteria increase at an exponential rate. During the 24 to 48 hours that
the dipsticks are incubating, bacteria counts can increase by orders of magnitude. If you
suspect the significant bacterial or fungal growth, it is better to act than to "wait
and see." |
Dissolved oxygen
| Collecting a fluid sample and immediately taking readings of
the dissolved oxygen level can be a quicker method of estimating the microbiological
activity in a fluid. Dissolved oxygen probes are readily available. |
| A reading of the dissolved oxygen level is taken immediately
after the fluid sample has been taken. The sample is left undisturbed for two hours, and
then a second reading is taken. The rate at which the dissolved oxygen concentration
decreases is related to the concentration of bacteria. As a rule of thumb, the second
reading should be greater than 6 PPM. If it is lower than 6 PPM, take action immediately
to control microbial growth. Otherwise, problems will be noticeable within two days. |
Catalase levels
| A kit is available that estimates microbial activity from the amount of
oxygen evolved from the action of the enzyme catalase on hydrogen peroxide. Some fluid
components and contaminants seem to interfere with results, but some users report useful
data. |
What are acceptable
levels of microbes?
| Most fluids will tolerate bacterial levels of 103 organisms /mL
with no adverse effects. However, water-diluted fluids can reach levels as high as 108
organisms/mL. There are also some fluids that are "bio-stable" that operate at
high bacterial levels without developing odors. There is no consensus on what level of
bacterial contamination is safe. It has been suggested that concentrations greater than 105/mL
should be controlled. |
|
| Fungal levels should be held to less than 100/mL. Fungal cells are
normally part of a mass of cells. The presence of even a small number of free-floating
cells is an indication of a larger number somewhere in the system that needs attention. |
|
| If counts are increasing with time, the fluid should be treated with a
biocide before problems are evident. It is much easier to keep counts at a low level by
early treatment than it is to bring counts down from a high level. When using a biocide,
always treat the system at the recommended level. Use of any biocide at low levels will
decrease its effectiveness. The user must read, understand, and follow all appropriate
instructions for the handling, storage and use of each biocide, as specified by the
biocide manufacturer, and must adhere to all regulatory requirements. |
How often should each test be
performed?
The chart below summarizes how often the most important fluid tests should be
performed, depending on the size of the sump.
Sump Class |
Sump
Size |
MRF
Evaluation Method |
Interval |
Miniature |
0.1
to 4 gallons |
visual
inspection |
daily |
_________ |
odor |
daily |
Small |
5 to 20 gallons |
visual inspection |
daily |
_________ |
odor |
daily |
concentration (sump level) |
daily |
Small-Medium |
26 to 80 gallons |
visual inspection |
daily |
__________ |
odor |
daily |
concentration (sump level) |
daily |
concentration (refractive index) |
weekly |
pH |
weekly |
Medium |
1001000 gallons |
visual inspection |
daily |
___________ |
odor |
daily |
concentration (refractive index) |
daily |
pH |
daily |
Large |
over 1000 gallons |
visual inspection |
daily |
__________ |
odor |
daily |
concentration (refractive index) |
daily |
concentration (acid) split or other |
twice weekly |
pH |
daily |
microbiological
(dissolved oxygen) |
twice
weekly |
microbiological
(culture) |
weekly |
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